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Vol. 53 - Alaska Resources Library and Information Services

Vol. 53 - Alaska Resources Library and Information Services

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Epibenthic density <strong>and</strong> biomass data were analyzed in two ways. First,<br />

mean biomass values were calculated for each major taxonomic group per<br />

cruise; these values were labeled mean catch per unit effort (CPUE) in<br />

units of gm-2. These data are presented in tabular form to show the<br />

relative importance of major fish <strong>and</strong> invertebrate groups in the<br />

samples. The second major analysis of epifaunal data was cluster<br />

analysis. Cluster analysis using EAP (1982) involved a square root<br />

transformation of all data <strong>and</strong> appropriate st<strong>and</strong>ardizations. Dissimilarities<br />

or distances among the entities (samples or species)<br />

were calculated using the Bray-Curtis Index (Bray <strong>and</strong> Curtis 1957).<br />

Formation of the two dendrograms <strong>and</strong> the two-way matrix of sample <strong>and</strong><br />

species groups involved flexible sorting with the addition of a step<br />

across distances re-estimation for the species groupings <strong>and</strong> the two-way<br />

matrix.<br />

Post-larval king crab densities <strong>and</strong> related physical <strong>and</strong> biological<br />

environmental variables were examined using correlation <strong>and</strong> multiple<br />

linear regression analyses. For the purpose of these analyses, king<br />

crabs were divided into four age groups: 1) young-of-the-year or 0+; 2)<br />

ages 1, 1+ <strong>and</strong> 2; 3) ages 2+ <strong>and</strong> 3; <strong>and</strong> 4) ages 3+ <strong>and</strong> older (3++). The<br />

four physical variables were: 1) depth; 2) bottom water temperature; 3)<br />

bottom water salinity; <strong>and</strong> 4) percent gravel in sediment samples. The<br />

biological variables used were the mean sample biomass values for nine<br />

taxa: 1) flatfishes; 2) roundfishes (all fish except Pleuronectidae); 3)<br />

polychaete worms; 4) shrimps (including p<strong>and</strong>alids <strong>and</strong> crangonids); 5)<br />

the sea star (Asterias amurensis); 6) the sea urchin (Strongylocentrotus<br />

droebachiensis); 7) sponge; 8) bryozoans; <strong>and</strong> 9) the sea onion (Boltenia<br />

ovifera). Biomass data were available for all of these taxa with the<br />

exception of bryozoan biomass from all quantitative trynet <strong>and</strong> rock<br />

dredge samples. Bryozoan biomass data were not always available due to<br />

the difficulty of separating this taxon from its substrate; however, the<br />

taxon was included in the analysis because of its apparent use as<br />

food by juvenile red king crabs (see Appendix F).<br />

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